| Nitroscanate (Ref: CGA 23654) |
![]() Last updated: 06/09/2025 |
![]() |
(Also known as: cantrodifene) |
|
|
|
Veterinary drug used to control and eliminate parasites | |
|---|---|---|
|
Used for the control parasitic infestations such as roundworm, tapeworm, fluke and hookworm | |
|
Dogs; Cats |
| Approval status |
|
Approved - legal class and availability depends on product and application | |
|---|---|---|
|
Approved |
| Chemical structure |
|
None | |
|---|---|---|
|
C₁₃H₈N₂O₃S | |
|
C1=CC(=CC=C1N=C=S)OC2=CC=C(C=C2)[N+](=O)[O-] | |
|
No data | |
|
SVMGVZLUIWGYPH-UHFFFAOYSA-N | |
|
InChI=1S/C13H8N2O3S/c16-15(17)11-3-7-13(8-4-11)18-12-5-1-10(2-6-12)14-9-19/h1-8H | |
|
Yes |
|
|
| Common Name | Relationship | Link |
|---|---|---|
| nitroscanate | - | ![]() |
| General status |
|
Antiparasitic, Medicinal drug, Anthelmintic | ||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
Nitroimidazole | ||||||||||||||
|
- | ||||||||||||||
|
- | ||||||||||||||
|
Synthetic | ||||||||||||||
|
Thought to act as an uncoupler of oxidative phosphorylation within the mitochondria of parasitic worms | ||||||||||||||
|
[Uncoupler of oxidative phosphorylation] | ||||||||||||||
|
19881-18-6 | ||||||||||||||
|
243-393-6 | ||||||||||||||
|
- | ||||||||||||||
|
- | ||||||||||||||
|
- | ||||||||||||||
|
Antiparasitic products, insecticides & repellents: Anthelmintics | ||||||||||||||
|
QP52AX01 | ||||||||||||||
|
No | ||||||||||||||
|
- | ||||||||||||||
|
272.28 | ||||||||||||||
|
- | ||||||||||||||
|
1-(4-isothiocyanatophenoxy)-4-nitrobenzene | ||||||||||||||
|
1-isothiocyanato-4-(4-nitrophenoxy)benzene | ||||||||||||||
|
|
||||||||||||||
|
- | ||||||||||||||
|
- | ||||||||||||||
|
- | ||||||||||||||
|
- | ||||||||||||||
| Commercial |
|
|
|||
|---|---|---|---|---|
|
Current | |||
|
1973, introduced | |||
|
|
|||
|
|
|||
|
Usually supplied in tablet form for oral administration | |||
|
Nitroscanate is synthesised through a multi-step chemical process involving the formation of an isothiocyanate functional group. The production begins with the preparation of a dithiocarbamic acid salt, which is reacted with an alkyl chloroformate in an aprotic solvent to form a carboalkoxydithiocarbamate intermediate. This intermediate, under controlled conditions and sometimes in the presence of a catalyst, undergoes thermal decomposition to yield nitroscanate. | |||
|
Published GHG data is not available for most pharmaceuticals. However, according to industry, global averages suggest producing 1 kg of a typical active pharmaceutical ingredient can range from 10 to 100 kg CO₂e for small molecule drugs and potentially up to 1000 kg CO₂e for complex biologicals such as vaccines, depending on the drug type, its formulation, complexity of synthesis, solvent recovery, and energy sources used. |
|
|
|
|
|
|
||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
110 | Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
- | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
1.58 X 1005 | Calculated | - | |||||||
|
5.2 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
High | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
| - | |||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
| Degradation |
|
|
|
|
||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
As this parameter is not normally measured directly, a surrogate measure is used: ‘Photochemical oxidative DT₅₀’. Where data is available, this can be found in the Fate Indices section below. | ||||||||||
|
- | ||||||||||
| Soil adsorption and mobility |
|
|
|
|
||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | ||||||||||
|
- | ||||||||||
|
- | ||||||||||
| Fate indices |
|
|
|
|
||||||||||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||||||||||||||||||||
|
|
- | - | - | |||||||||||||||||||||||||
|
- | - | |||||||||||||||||||||||||||
| Known soil and groundwater metabolites |
None
| Other known metabolites |
|
|
|
|
||||
|---|---|---|---|---|---|---|---|
| 4-amino-4-nitrodiphenyl ether Note: Possible animal and human metabolite but not confirmed |
ANDE | - | - | ||||
| 4-acetamido-4-nitrodiphenyl ether Note: Possible animal and human metabolite but not confirmed |
AcNDE | - | - | ||||
| 4-acetamido-4-nitrosodiphenyl ether Note: Possible animal and human metabolite but not confirmed |
- | - | - | ||||
| 4-acetamido-4-hydroxylaminodiphenyl ether Note: Possible animal and human metabolite but not confirmed |
- | - | - | ||||
| 4-acetamido-4-acetohydroxamicdiphenyl ether Note: Possible animal and human metabolite but not confirmed |
- | - | - | ||||
| 4-acetamido-4-for-mohydroxamicdiphenyl ether Note: Possible animal and human metabolite but not confirmed |
- | - | - | ||||
| 4-acetamido-4-acetylaceto-hydroxamicdiphenyl ether Note: Possible animal and human metabolite but not confirmed |
- | - | - |
|
|
| Terrestrial ecotoxicology |
|
|
|
|
||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
> 3500 | Q3 Q = Miscellaneous data from online sources Rat3 = Unverified data of known source |
Low | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
| - | |||||||||||
|
- | - | - | ||||||||
| - | |||||||||||
|
|
- | - | - | |||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
|
- | - | - | |||||||
|
- | ||||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - | |||||||
|
- |
|
- | - | - | ||||||
|
- | ||||||||||
| Aquatic ecotoxicology |
|
|
|
|
||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | - | - |
|
- | - | - | |||
|
- | - | - | ||||||||
|
|
| General |
|
|
|
|
||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
|
High (class III) | - | - | ||||||||
|
> 3500 | Q3 Q = Miscellaneous data from online sources Rat3 = Unverified data of known source |
Low | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
- | - | - | ||||||||
|
|
- | |||||||||
|
- | ||||||||||
|
Partly absorbed from the gastrointestinal tract, with the majority of the dose being eliminated in the faeces. The remainder of the dose is metabolised and excreted in the urine. | Q4 Q = Miscellaneous data from online sources 4 = Verified data |
- | ||||||||
| Health issues |
|
|
||||||||||||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
|
May cause diarrhoea, and lethargy | ||||||||||||||||||||||||||||
| Handling issues |
|
|
|||
|---|---|---|---|---|
|
No information available | |||
|
- | |||
|
Not listed (Not listed) | |||
|
- | |||
|
- | |||
|
- |
|
|
|
|
||
|---|---|---|---|
|
nitroscanate | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
nitroscanato | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- | ||
|
- |
| Record last updated: | 06/09/2025 |
| Contact: | aeru@herts.ac.uk |
| Please cite as: | Lewis, K.A., Tzilivakis, J., Warner, D. and Green, A. (2016) An international database for pesticide risk assessments and management. Human and Ecological Risk Assessment: An International Journal, 22(4), 1050-1064. DOI: 10.1080/10807039.2015.1133242 |
© Copyright University of Hertfordshire, 2006-2026. All Rights Reserved
Your use of this website and its various databases is subject to the terms detailed in the University of Hertfordshire’s copyright and IPR statement that can be found at https://www.herts.ac.uk/about-us/legal. In addition, your use of this website and its various databases is subject to the terms of this additional Copyright Statement and the database Conditions of use document. Unless explicitly stated otherwise, the content of this website and databases are owned and controlled by the University of Hertfordshire. Site content, including its selection and arrangement, is owned by the University of Hertfordshire and is protected by copyright and other laws. Except as otherwise expressly permitted under copyright law or within the database Conditions of Use document, the content of this site may not be copied, reproduced, republished, downloaded, posted, broadcast or transmitted in any way without first obtaining the University of Hertfordshire’s written permission. By using our databases the user is deemed to have agreed to comply with all of the terms and conditions as described above and within all relevant documentation.





